TW202107015A - Combustible waste blowing device and operation method therefor - Google Patents

Abstract

Provided is a combustible waste blowing device and an operation method therefor that can suppress landing combustion of combustible waste, as well as an excessive change in the state of a flame generated in a cement kiln burner even when the use ratio of combustible waste varies. This combustible waste blowing device comprises a combustible waste flow path that is disposed inside an air flow path in the innermost shell, is arranged so as to be parallel with the axial direction of a cement kiln burner device, and allows the flow of combustible waste to pass therethrough. The combustible waste flow path has a slanted surface in the vicinity of a suction port, said slanted surface being slanted upward toward the suction port such that the flow-path width in the vertical direction becomes narrower with increasing proximity to the suction port.

Description

Combustible waste blowing device and operation method thereof

The present invention relates to a combustible waste blowing device attached to a burner for cement kilns, etc., and an operating method thereof.

Combustible wastes such as waste plastics, wood chips, and automobile shredder residue (ASR: Automobile Shredder Residue) have enough heat to be used as fuel for burning. Therefore, in the rotary kiln used for the firing of cement clinker, the effective use of combustible waste as the main fuel, namely the auxiliary fuel of pulverized coal, is being promoted. Hereinafter, the rotary kiln used for the firing of cement clinker is called "cement kiln".

Previously, research was under way to use the fuel cycle of combustible waste in cement kilns in the calcination furnace at the end of the kiln, which has less impact on the quality of cement clinker. However, as the amount of combustible waste used in the calciner is close to saturation, the use of technology in the main burner installed in the front of the kiln is being researched and developed.

Here, when combustible waste is used as an auxiliary fuel in the main burner of the cement kiln (hereinafter referred to as the "burner for cement kiln"), there may be combustible waste emitted from the burner for the cement kiln. The situation where the cement clinker that has landed in the cement kiln continues to burn (hereinafter referred to as "land burning"). When the land burning situation occurs, the surrounding cement clinker where the land burning of combustible waste occurs is reduced and fired, resulting in whitening of the cement clinker or abnormal cement clinker generation reaction.

In order to avoid the burning of combustible waste sprayed from cement kiln burners, several methods are considered. One method is to make the floating state of the combustible waste in the cement kiln continue for a long time and end the combustion of the combustible waste in the floating state. Another method is to form a suitable combustion environment for combustible waste and accelerate the burning rate of combustible waste. Yet another method is to make the combustible waste land on the far side of the cement kiln (kiln tail side), and terminate the combustion of the combustible waste before the clinker raw material reaches the main reaction zone of the cement clinker formation reaction.

For example, in Patent Document 1 below, as a technique for reducing energy consumption by landing combustible waste on the far side (kiln tail side) of a cement kiln, there is a structure for inputting combustible waste. It freely rotatably supports the end of the rotary kiln, and is composed of a plurality of combustible waste burners with a protrusion of 200-500 mm from the end wall of the front of the kiln. In addition, the following Patent Document 2 discloses a rotary kiln for cement manufacturing as a technique to avoid the disadvantages caused by the blowing of combustible waste and to burn combustible waste more efficiently. The outer peripheral surface of the burner is positioned vertically above the main fuel burner and is provided with an auxiliary burner that blows the combustible waste at an upward blowing angle relative to the main fuel burner. [Prior Art Literature] [Patent Literature]

[Patent Document 1] Japanese Patent Laid-Open No. 2003-90522 [Patent Document 2] Japanese Patent Laid-Open No. 2011-207682

[The problem to be solved by the invention]

Generally, the ratio of the usage amount of pulverized coal that is the main fuel in the burner for cement kilns to the usage amount of auxiliary fuel that is combustible waste varies depending on the availability and properties of these fuels. The change of fuel composition also avoids changing the quality of cement clinker, and requires technology to stabilize the state of the flame from the burner used in the cement kiln. However, in the method of Patent Document 1 or 2, there is a problem that the state of the flame from the burner for a cement kiln greatly changes depending on the amount of combustible waste blown into the cement kiln and the blowing angle.

In view of the above-mentioned problems, the present invention aims to provide a combustible waste blowing device and an operating method thereof, which can be used when combustible waste is used as an auxiliary fuel in the manufacture of cement clinker. Suppress the local burning of combustible waste, and even if the use rate of combustible waste changes, it can also prevent excessive changes in the state of the flame from the burner for cement kilns. [Technical means to solve the problem]

The inventors of the present invention conducted intensive research on the above-mentioned problems and found that in a combustible waste blowing device that is attached to a burner device for cement kilns and is equipped with a blowing port near the center of the burner device for cement kilns, if The vertical lower side (bottom side) in the combustible waste duct near the blowing port (hereinafter referred to as the "combustible waste flow path") is provided with an upward slope toward the blowing port to solve the above problem. .

That is, the present invention is a combustible waste blowing device, which is provided with at least one air flow path inside the flow path for solid powder fuel, and can be attached to a burner device for cement kilns, and is characterized in that it has The combustible waste flow path is arranged on the inner side of the air flow path of the innermost shell, and is arranged in parallel with the axial direction of the burner device for the cement kiln to convey the combustible waste flow, and The combustible waste flow path has an upward slope toward the blowing port near the blowing port so that the width of the flow path in the vertical direction becomes narrower as it approaches the blowing port. In addition, hereinafter, the "inclined surface having an upward slope toward the blowing port" is sometimes referred to as the "upward slope". In addition, the "blowing inlet" corresponds to the end of the cement kiln side of the burner device for the cement kiln.

"Combustible waste" in this manual is as mentioned above, and refers to the general waste and industrial waste which is composed of waste plastic, wood chips, ASR or organic matter such as meat and bone meal or biomass as the main body. The fuel used for the burning of the fuel is assumed to be used together with the solid powder fuel (main fuel) as the fuel for the burner. More specifically, the particle size of combustible waste is 30 mm or less. In addition, "biomass" refers to organic resources derived from organisms that can be used as fuels other than fossil fuels. For example, the crushed material of discarded tatami mats, the crushed material of construction waste wood, wood powder and sawdust, etc. belong to biomass.

As described above, the combustible waste flow path has an upward slope near the blowing port (the end of the cement kiln side). The upward slope is provided at the bottom of the combustible waste flow path that is located on the lower side of the vertical direction than the horizontal plane including the axis when the combustible waste flow path is cut along the plane orthogonal to the axis. By providing this upward slope in the combustible waste flow path, combustible waste is sprayed upward in the cement kiln. As a result, the combustible waste (auxiliary fuel) blown into the cement kiln from the combustible waste blowing device can continue to float in the cement kiln for a long time and be moved to the far side of the cement kiln (kiln tail side) ), can end the combustion without hindering the cement clinker formation reaction.

The inclined surface may have an end on the opposite side of the blowing port in the axial direction of the combustible waste flow path at a distance of 150 mm to 2000 mm from the blowing port, and an elevation angle of 1° to 4°. Furthermore, the end of the inclined surface on the side of the blowing port can be set to coincide with the blowing port, or it can be set to a position about a few centimeters away from the blowing port along the axial direction, and a flat surface is formed between the inclined surface and the blowing port. constitute.

By setting the installation position and elevation angle of the inclined surface within the above-mentioned numerical range, in the combustible waste flow path of the usual size with an inner diameter of 150 mm to 200 mm, the blowing port when the upward inclined surface is installed can be used. area S (cm ²⁾ relative to the area S ₀ of the time of blowing port upward slope of the case is not provided (cm ²⁾ the ratio S / S ₀ is larger than 0.5. Thereby, the combustible waste stream can be released into the cement kiln from the combustible waste stream without experiencing excessive pressure loss.

The combustible waste blowing device may be provided in the combustible waste flow path at the portion where the inclined surface is formed to allow an air flow (hereinafter referred to as "auxiliary air flow") to flow toward the axis of the combustible waste flow path The above-mentioned air inlet in the combustible waste flow path (hereinafter referred to as the "auxiliary air inlet"), and The auxiliary air inlets are arranged at a plurality of locations in the circumferential direction.

In particular, the auxiliary air inlets are preferably arranged at a plurality of locations, which include the combustible waste flow path when cut along a plane orthogonal to the axis of the combustible waste flow path in the vertical direction. The horizontal plane of the axis.

According to the above configuration, the auxiliary air flow flows toward the axis of the combustible waste flow path at the location where the above-mentioned inclined surface (upward slope) is formed, near the blowing port of the combustible waste flow path, so the combustible waste is combustible The blowing port of the waste flow path sprays upwards, and sprays on the side of the cement kiln while spreading moderately in the vertical direction. Thereby, the mixing state of the main fuel and combustible waste (auxiliary fuel) blown into the cement kiln from the solid powder fuel at the position surrounding the blowing port of the combustible waste blowing device becomes good, and The high-temperature air (secondary air) supplied from the cement cooler to the cement kiln is also well mixed with the main fuel. By these simultaneous processes, combustible waste can be formed in the cement kiln. The main fuel can be mixed appropriately. And an environment that burns efficiently. As a result, a suitable combustion environment for combustible waste is formed. Therefore, as described above, the combustion speed of combustible waste in the cement kiln can be accelerated, and the combustion of combustible waste can be completed in a floating state.

The combustible waste blowing device is provided with an auxiliary air flow path provided in parallel with the combustible waste flow path at a position outside the combustible waste flow path, The auxiliary air flow path may be connected to the combustible waste flow path via the auxiliary air inflow port. On the other hand, the upstream side of the auxiliary air flow inlet may be blocked from the combustible waste flow path.

The air flow rate passing through the auxiliary air flow path is preferably configured as follows: the combustible waste flow passing through the combustible waste flow path may be reduced in the axial direction and then sprayed upward in the vertical direction, Independently control during operation. As a result, even if the types or usage rates of the solid powder fuel (main fuel) and combustible waste (auxiliary fuel) used are changed, they can be easily adjusted to maintain the cement kiln burner while continuing to operate. The best flame state of burners for cement kilns.

In the above configuration, the combustible waste flow path is provided with a plurality of auxiliary air inlets connected to the auxiliary air flow path at a predetermined distance from the blowing inlet. At this time, the flow rate of the auxiliary air flowing into the combustible waste flow path through each auxiliary air inlet is preferably such that the auxiliary air flow path can be independently controlled by a blower or a flow adjustment valve connected to each auxiliary air flow path. The way of control is constituted.

More preferably, it is the air flow rate that flows into the combustible waste flow path from the auxiliary air inlet at the lower side of the vertical direction when the horizontal plane including the axis center is cut along the plane orthogonal to the combustible waste flow path. (Referred to as "upward auxiliary air flow rate") is the air flow rate (referred to as "downward auxiliary air flow rate") that flows in from the upper side of the vertical direction of the above horizontal plane. As a result, combustible waste is discharged from the blowing port of the combustible waste blowing device at an elevation angle greater than the elevation angle of the upward slope. Therefore, as described above, the floating state of combustible waste in the cement kiln continues for a long time , And can end the combustion of combustible waste in a floating state.

Especially by adjusting the air flow from the auxiliary air inlet to the combustible waste flow path, or further adjusting the ratio of the upward auxiliary air flow to the downward auxiliary air flow, even the ratio of the auxiliary fuel used in the burner for cement kilns [(Auxiliary Fuel)/(Main Fuel + Auxiliary Fuel)], and/or the type or properties of combustible waste used as auxiliary fuel changes, and it can also be controlled to avoid the shape of the flame from the burner used in the cement kiln Or the temperature distribution changes.

In addition, by adjusting the ratio of the upward auxiliary air flow rate to the downward auxiliary air flow rate, the elevation angle when the combustible waste is discharged into the cement kiln can be substantially adjusted. That is, when the elevation angle of the inclined surface (upward inclined surface) is insufficient, by increasing the ratio of the upward auxiliary air flow rate, the elevation angle of the discharged combustible waste stream can be substantially increased, and the combustibility in the cement kiln can be improved. The effect of the floating state of the waste is continuous.

Furthermore, the auxiliary air inflow port may be arranged at a plurality of locations, and these locations are arranged in a horizontal direction across the vertical surface including the axis when the combustible waste flow path is cut along the plane orthogonal to the axis. As a result, the combustible waste stream receives the same auxiliary air flow from the left and right directions, thereby being narrowed not only in the vertical direction (up and down direction), but also in the left and right directions, and it is well generated in the whole circumference direction of up, down, left, and right. The state where the combustible waste in the cement kiln after being blown out from the combustible waste blowing device is floating and spreading. Thereby, a good mixing state of the above-mentioned main fuel or secondary air and combustible waste can be formed more reliably throughout the entire circumference.

The auxiliary air inlet may also be arranged in a range of 10 mm to 600 mm away from the blowing inlet of the combustible waste flow path. If it is in this range, in the combustible waste flow path with the normal size of 150 mm～200 mm inner diameter and the normal primary air flow rate (60 m ³ /min～120 m ³ /min) is used for combustible waste The blowing device can promote the completion of combustion of combustible waste in a floating state. Furthermore, the auxiliary air inlets may be arranged in a circle around one circle, or two or more circles, that is, arranged in a plurality of rows.

The shape of the auxiliary air inlet is not limited as long as the fluid of the combustible waste conveyed by the primary air (combustible waste stream) is narrowed in the axial direction. Furthermore, from the viewpoint of easily obtaining the narrowing effect by the auxiliary air, the auxiliary air inlet is preferably a circular shape with a diameter of 5 mm to 25 mm, or the circumferential direction is the long side, and the flow direction is the short. Rectangle (long strip) with the short side of 3 mm～15 mm. When the auxiliary air inlets are circular, they may be arranged at equal intervals on the circumference, or may be arranged at non-equal intervals. In the latter case, it is better to set the combustible waste flow path near the intersection (top and bottom) of the vertical axis and the inner surface of the combustible waste flow path when the combustible waste flow path is cut along the plane orthogonal to the axis. Non-equal interval configuration with higher distribution.

Furthermore, the auxiliary air inlet may also be provided with an auxiliary air feeder, which can prevent the flow of the combustible waste into the combustible waste flow path when the combustible waste flow is transported in the combustible waste flow path as a reference. The inflow angle of the above-mentioned auxiliary air flow is adjusted.

Furthermore, the present invention is an operating method of the above combustible waste blowing device, characterized in that the combustible waste stream is sprayed upward from the combustible waste flow path in a vertical direction relative to the horizontal plane.

At this time, it is preferable to give an elevation angle during normal operation by an upward slope, and to set the upward auxiliary air flow inflow from the lower side of the vertical direction of the horizontal plane to be greater than the downward auxiliary air flow inflow from the upper side of the vertical direction of the horizontal plane. . In this case, the ratio of the above-mentioned downward auxiliary air flow rate to the above-mentioned upward auxiliary air flow rate is preferably set to 0.5 to 1.0. Furthermore, when the ratio of the downward auxiliary air flow rate to the upward auxiliary air flow rate is 1.0, the auxiliary air will not exert an effect on the elevation angle of the above-mentioned combustible waste stream, but by narrowing the combustible waste stream, The effect of combustible waste spreading in the cement kiln can be obtained.

^{In addition, the total amount (m 3} /min) of air flow into the combustible waste flow path from the auxiliary air inlet can be set as the primary air flow rate (m ³ /min) that circulates in the combustible waste flow path. 5%～65% by volume. Furthermore, in the operating method of the combustible waste blowing device, there is no restriction on the primary air flow rate circulating in the combustible waste flow path, and normal operating conditions can be adopted.

Moreover, the inflow angle of the auxiliary air flow flowing into the combustible waste flow path can be set to be greater than 0° and 90° based on the transport direction of the combustible waste flow transported in the combustible waste flow path. the following. According to this structure, the auxiliary air flow can be prevented from colliding in the reverse direction with respect to the conveying direction of the combustible waste stream. Therefore, the flow of the combustible waste stream is not excessively hindered, and the combustible waste stream can be reduced in the axial direction. Blow out from the inlet. [Effects of Invention]

According to the combustible waste blowing device and its operating method of the present invention, it is possible to arbitrarily change the solid powder fuel (main fuel) and waste while maintaining the state of the flame from the burner for the cement kiln in an optimal state. The ratio of use of combustible waste (auxiliary fuel) such as plastic chips, and the effective use of combustible waste (auxiliary fuel) with a particle size of 30 mm or less.

Hereinafter, embodiments of the combustible waste blowing device and its operating method of the present invention will be described with reference to the drawings. Furthermore, the following drawings are schematically represented, and the size ratio in the drawings is not consistent with the actual size ratio.

Fig. 1 is a diagram schematically showing the central part of the front end of an embodiment of a burner device for a cement kiln equipped with a combustible waste blowing device of the present invention. In Figure 1, (a) is a cross-sectional view of a cement kiln burner device including an attached combustible waste blowing device, and (b) is a cement kiln including an attached combustible waste blowing device The longitudinal cross-sectional view of the burner device. Furthermore, the cross-sectional view refers to the cross-sectional view of the burner device for the cement kiln cut along a plane orthogonal to the axial direction of the same device. The longitudinal cross-sectional view refers to the cross-sectional view of the cement kiln. A cross-sectional view of the burner device cut along a plane parallel to the axial direction of the same device.

Furthermore, in Fig. 1, the axial direction (direction of the primary air flow) of the burner device for the cement kiln is set to the Y direction, the vertical direction is set to the Z direction, and the direction orthogonal to the YZ plane is set to the X direction , And set the coordinate system. Hereinafter, the description will be made with reference to the XYZ coordinate system as appropriate. If the XYZ coordinate system is used for description, Fig. 1(a) corresponds to the cross-sectional view when the cement kiln burner device is cut along the XZ plane, and Fig. 1(b) corresponds to the cement kiln burner device along YZ The cross-sectional view when the plane is cut off. In more detail, Fig. 1(b) corresponds to a cross-sectional view of the burner device for the cement kiln cut along the YZ plane at the end of the cement kiln side (the front end of the burner device for the cement kiln).

Furthermore, the XYZ coordinate systems illustrated in FIGS. 2A to 4B and FIGS. 6 to 7 described below are the same axis relationship as the XYZ coordinate system illustrated in FIG. 1.

As shown in Figure 1(a), the combustible waste flow path 3 of the combustible waste blowing device 2 attached to the cement kiln burner device 1 is arranged in concentric circles in the cement kiln burner device 1 The flow path 21 for solid powder fuel and at least one air flow path 22 arranged inside adjacent to the flow path 21 for solid powder fuel. Adjacent to the combustible waste flow path 3 of the combustible waste blowing device 2, an oil flow path 31 for supplying heavy oil or the like can be arranged inside the air flow path 22.

In addition, in FIG. 1, the air flow path 22 has the turning wing 22a as a turning means at the end part (in the vicinity of the blowing inlet side) of a cement kiln. That is, the air flow ejected from the air flow path 22 forms a revolving air flow located inside with respect to the solid powder fuel flow ejected from the solid powder fuel flow path 21. The rotating wing 22a may be configured to be able to adjust the angle of rotation before the start of the operation of the burner device 1 for the cement kiln.

As shown in Fig. 1(b), inside the burner device 1 for a cement kiln, in the vertical direction (Z direction), the bottom surface of the combustible waste flow path 3 forms an upward slope 8 near the inlet side. The upward slope 8 corresponds to the "inclined surface". Furthermore, in this embodiment, as shown in FIG. 1(b), inside the burner device 1 for a cement kiln, an auxiliary air flow path 4 is provided on the outside of the combustible waste flow path 3, and the auxiliary air can pass through the auxiliary air The inflow port 5 flows into the combustible waste flow path 3. This aspect will be described below with reference to FIGS. 2A and 2B.

The upward slope 8 is not limited as long as the bottom surface of the combustible waste flow path 3 has a slope. As an example, it can be formed by gradually increasing the thickness of the inner wall corresponding to the bottom of the combustible waste flow path 3 in a predetermined area in the Y direction, and the inner wall surface of the combustible waste flow path 3 itself The upward slope 8 is formed. As another example, in a predetermined area in the Y direction, another member whose height gradually changes along the Y direction is provided on the inner wall corresponding to the bottom of the combustible waste flow path 3, and the surface of the other member is formed upward Incline 8. In either case, the result of forming the upward slope 8 in the combustible waste flow path 3 is formed in such a way that the width of the combustible waste flow path 3 in the vertical direction becomes narrower as it approaches the blowing inlet.

2A and 2B are diagrams schematically showing the front end of an embodiment of the combustible waste blowing device 2 of the present invention. Fig. 2A is a longitudinal cross-sectional view of the combustible waste blowing device 2, and Fig. 2B is a cross-sectional view of Fig. 2A where the Y coordinate is Y1 (hereinafter simply referred to as "the position of Y1") (corresponding to (a )), and the cross-sectional view (corresponding to (b)) at the position where the Y coordinate is Y2 (hereinafter referred to as "the position of Y2"). The position of Y1 corresponds to the vicinity of the front end of the combustible waste flow path 3 (that is, near the blowing inlet), and the position of Y2 corresponds to the upstream side of the position of Y1 and is far from the front end of the combustible waste flow path 3.

As shown in FIG. 2A, an upward slope 8 is formed on the bottom surface of the combustible waste flow path 3. The elevation angle φ (inclination angle) of the upward slope 8 relative to the horizontal plane (XY plane) is 1° to 4°. In addition, the upward inclined surface 8 is formed in the Y direction from a position 150 mm to 2000 mm away from the blowing port toward the blowing port.

Furthermore, in this embodiment, as shown in FIG. 2B, the auxiliary air flow path 4 is arranged on the outer side of the combustible waste flow path 3. In more detail, the auxiliary air flow path 4 in this embodiment is arranged concentrically on the outer side of the cylindrical combustible waste flow path 3, and is divided into the auxiliary air flow path 4-1 on the vertical upper side by the partition member 6 2 of the auxiliary air channels 4-2 on the vertical lower side.

As shown in Figure 2B(b), an auxiliary air inlet 5 connecting the auxiliary air flow path 4 (4-1, 4-2) and the combustible waste flow path 3 is provided at the Y2 position to allow the flow through The auxiliary air of the auxiliary air flow path 4 is configured to flow into the combustible waste flow path 3 toward the axis 3c of the combustible waste flow path 3. In this embodiment, the combustible waste flow path 3 is provided with auxiliary air inlets 5 (5-1 to 5-10) arranged at 10 locations in the circumferential direction at the position Y2. In more detail, five auxiliary air inlets (5-1 to 5-3, 5-9, 5-10) are arranged on the auxiliary air flow path 4-1 side (vertical upper side), and the auxiliary air flow path 4 Five auxiliary air inlets (5-4 to 5-8) are arranged on the -2 side (vertical lower side).

Furthermore, in Fig. 2A, for the convenience of illustration, only the auxiliary air inlets (5-1, 5-6) of the 10 auxiliary air inlets 5 (5-1～5-10) appear in the figure. .

A dedicated blower (not shown) or a flow adjustment valve (not shown) is connected to the auxiliary air flow paths (4-1, 4-2), and each auxiliary air flow path (4-1, 4-2) can be independently controlled. 4-2) The auxiliary air flow rate.

Fig. 3 is a schematic representation of the front end of one embodiment of the combustible waste blowing device 2 of the present invention shown in Fig. 2A, enlarging and schematically showing the periphery of the auxiliary air inlet (5-1, 5-6) The schema.

As shown in FIG. 3, an auxiliary air inlet 7 is provided at the auxiliary air inlet (5-1, 5-6) connecting the combustible waste flow path 3 and the auxiliary air flow path 4. The auxiliary air feeder 7 is provided with an inflow angle θ for the direction of the auxiliary air AA flowing into the combustible waste flow path 3 with respect to the direction of the combustible waste RF flowing in the combustible waste flow path 3 (Θ1, θ2) to control. Furthermore, in FIG. 3, the situation of the inflow angle θ=θ1 and the situation in which the inflow angle θ=θ2 is set schematically are various aspects of the auxiliary air feeding member 7.

The inflow angle θ can be set to be greater than 0° and 90° or less. When the inflow angle θ of the auxiliary air AA is 0°, the effect of changing the flow of the combustible waste RF by the auxiliary air AA is almost impossible to obtain, and when the inflow angle θ exceeds 90°, the auxiliary air AA It will cause the flow of combustible waste RF to slow down and be over-stirred, so they are all poor.

4A and 4B are diagrams schematically showing the front end of another embodiment of the combustible waste blowing device 2 of the present invention. Fig. 4A is a longitudinal cross-sectional view of the combustible waste blowing device 2 similar to Fig. 2A, Fig. 4B is a cross-sectional view (corresponding to (a)) at the position Y1 in Fig. 4A, similarly to Fig. 2B, and The cross-sectional view at the position of Y2 (corresponding to (b)). Furthermore, for convenience of illustration, the auxiliary air inlet 5 is not shown in FIG. 4A.

In the embodiment shown in FIG. 4B, the combustible waste flow path 3 is provided with auxiliary air inlets 5 (5-11 to 5-16) arranged at six locations in the circumferential direction at the position Y2. In addition, the combustible waste flow path 3 has dedicated auxiliary air flow paths (4-3 to 4-8) for each auxiliary air inlet (5-11 to 5-16). In this way, a dedicated blower (not shown) or a flow control valve (not shown) is connected to the auxiliary air flow paths 4-3 to 4-8, respectively, so that the supply to each auxiliary air flow path (4 -3～4-8) The configuration of auxiliary air flow. This aspect will be described with reference to FIG. 5.

Fig. 5 is a diagram schematically showing an example of the structure of the combustible waste blowing device shown in Fig. 4. The combustible waste blowing device 2 shown in Fig. 5 is constructed with emphasis on ease of control, and is equipped with 3 blowers (F1 to F3) and 6 flow control valves (B113, B114, B118, B135, B136, B137). The flow control valves (B113, B114, B118, B135, B136, B137) are constituted by, for example, air valves.

The combustible waste RF supplied to the combustible waste conveying pipe 12 is supplied to the combustible waste flow path 3 of the combustible waste blowing device 2 by the air flow formed by the blower F1. The air supplied from the blower F2 is supplied to the auxiliary air flow path 4 (4-3, 4-4, 4-8) via the air pipe 11 as the auxiliary air AA. In more detail, the air pipe 11 is branched by three branch pipes (113, 114, 118), and each branch pipe is connected to the above three auxiliary air flow paths (4-3, 4-4, 4-8). . Similarly, the air piping 13 for supplying auxiliary air AA from the blower F3 is branched by 3 branch pipes (135, 136, 137), and 3 auxiliary air flow paths (4-5, 4-6, 4-7) Connected.

Each branch pipe (113, 114, 118, 135, 136, 137) is provided with variable flow adjustment valves (B113, B114, B118, B135, B136, B137), by adjusting the The opening degree can independently control the flow of auxiliary air AA circulating in each branch pipe (113, 114, 118, 135, 136, 137).

That is, in the case of the combustible waste blowing device 2 shown in FIGS. 4A, 4B, and 5, an auxiliary air inlet 5 is provided corresponding to each auxiliary air flow path 4 (4-3 to 4-8) (5-11～5-16), so each auxiliary air inlet 5 (5-11～5-16) can independently control the flow of auxiliary air AA. Thereby, the state of the flame from the burner for the cement kiln can be maintained in an optimal state, and the use ratio of solid powder fuel (main fuel) and combustible waste (auxiliary fuel) can be easily changed.

Furthermore, an upward slope 8 is formed on the bottom surface near the blowing port of the combustible waste flow path 3, so that the combustible waste flow can be vertically upward (+Z direction) from the combustible waste flow path 3 compared to the horizontal plane (XY plane). Squirting. In this way, the floating state of combustible waste in the cement kiln can be sustained for a long time.

That is, as shown in FIG. 6, the combustible waste blowing device 2 of the present invention may have an upward slope 8 on the bottom surface of the combustible waste flow path 3, and it does not have the auxiliary air flow path 4 and the auxiliary air inflow port 5. However, like the combustible waste blowing device 2 shown in FIG. 1, the auxiliary air flow path 4 and the auxiliary air inflow port 5 are provided so that the auxiliary air AA flows in the direction of the axis of the combustible waste flow path 3. The effect of making the combustible waste flow further straight upward can be adjusted, so the effect of making the floating state of the combustible waste RF in the cement kiln into a suitable state can be further improved.

The inventors performed a combustion simulation (software: manufactured by ANSYS JAPAN, FLUENT) of a cement kiln burner device 1 equipped with a combustible waste blowing device 2 to perform a flame shape from a cement kiln burner and a cement kiln Analysis of the gas temperature distribution in the internal gas, the oxygen concentration distribution in the cement kiln, the degree of turbulence in the airflow in the cement kiln, etc., and found the basics for optimizing the control factor for blowing combustible waste into the device 2 Limit the scope.

Fig. 7 is a schematic map model of Fig. 1 and shows the structure of the cement kiln burner device 1 including the combustible waste blowing device 2 used in the simulation. The burner device 1 for cement kiln shown in FIG. 7 has the structure shown in FIG. 1 and further includes an air flow path 23 arranged on the outside of the solid powder fuel flow path 21 and provided with a rotary wing 23a, and an air flow path 23 arranged on the air The air flow path 24 on the outer side of the flow path 23. The air flow path 24 forms a flow path that directly enters the air flow. That is, the burner device 1 for a cement kiln that is the subject of simulation verification is shown in Figure 7(a). It is a so-called 4-channel burner device, which is equipped with an air flow path 22 that forms a revolving air flow from the inside, forming a revolving There are a total of four flow paths for the solid powder fuel flow path 21 for the main fuel flow, the air flow path 23 for forming the revolving air flow, and the air flow path 24 for forming the straight air flow.

Furthermore, the embodiment 1 described below is a cement kiln burner device 1 shown in FIG. 7 that does not have the auxiliary air flow path 4 and the auxiliary air inlet 5, which corresponds to the cement kiln burner device shown in FIG. 6 The device 1 is a 4-channel type.

The following Table 1 is an example of the basic limited range of the combustible waste blowing device 2 found under the specifications and operating conditions of the following cement kiln burner device 1. In addition, Table 1 corresponds to the embodiment of the combustible waste blowing device 2 illustrated in FIG. 2.

＜Specifications of burner device 1 for cement kiln＞ Number of channels: 4 channels (from the innermost shell side, it is the revolving air flow, the revolving main fuel flow, the revolving air flow, and the straight air flow) Combustible waste blowing device 2: It is arranged inside the air flow path 22 that forms a rotating air flow, and is attached to the lower side of the axis of the burner device 1 for the cement kiln. Diameter of the front end of the burner of the burner device 1 for cement kiln: 700 mm The inner diameter of the blowing port of the combustible waste blowing device 2: 175 mm The area where the upward slope 8 is formed: the area from the blowing port (end) of the combustible waste flow path 3 that is advanced 300 mm in the -Y direction to the blowing port (end) Auxiliary air inlet 5: 5 circular holes with a diameter of 16 mm each on the upper and lower sides of the vertical direction (with respect to the vertical axis at an interval of 30° within a range of ±60°)

<Operation conditions of burner device 1 for cement kiln> Burning amount of main fuel C flowing through flow path 21 for solid powder fuel: 12 t/h Treated amount of waste plastic (soft plastic) as combustible waste RF: 5 t/hour as flammable waste RF waste plastic size: punching a 0.5 mm sheet into a circular sheet with a diameter of 30 mm. Primary air flow rate (a total of 4 channels) and temperature: 15000 Nm ³ /Hour, 30°C secondary air flow and temperature: 100000 Nm ³ /hour, 900°C Primary air flow and temperature from combustible waste blowing device 2: 5000 Nm ³ /hour, 30°C from combustible waste blowing The blowing method and temperature of auxiliary air AA into the device 2: add auxiliary air AA with the primary air flow from the combustible waste blowing device 2 as the above value, 30°C

[Table 1] Figure 7 Cement Kiln Burner Device 1 Elevation angle of upward slope 8 φ 1°≦φ≦4° Auxiliary air flow The primary air volume of the combustible waste blowing device 2 is 5% to 65% by volume The ratio of the auxiliary air flow in the upper and lower directions r (Downward auxiliary air flow rate)/(upward auxiliary air flow rate) 0.5～1.0 Position of auxiliary air inlet 5 10 mm～600 mm away from the blowing inlet (end) of combustible waste flow path 3 Inflow angle of auxiliary air θ 0°＜θ≦90°

In Table 1, as the basic limited range, the elevation angle φ (°) of the upward slope 8 and the flow rate of auxiliary air AA (volume% of the total auxiliary air flow rate relative to the primary air flow rate of the combustible waste blowing device 2) are listed, The ratio of the flow rate of auxiliary air flowing in from the vertical upper side of the horizontal plane containing the axis to the flow rate of each auxiliary air flowing in from the vertical lower side of the horizontal plane containing the axis r[(downward auxiliary air flow)/(upward auxiliary air flow)] , The distance between the auxiliary air inlet 5 and the end of the combustible waste flow path 3 (mm), and the inflow angle (°) of the auxiliary air AA flowing from the auxiliary air inlet 5 into the combustible waste flow path 3.

Among the above items, what is important is the elevation angle φ of the upward slope 8, the flow rate of the auxiliary air AA, the position of the auxiliary air inlet 5, and the ratio r of the amount of auxiliary air AA in the upper and lower directions.

The reason is that, as described above, in order to facilitate the adjustment of a stable flame even if the fuel composition used in the cement kiln burner device 1 changes, it is necessary to form combustible waste RF, main fuel C, and The secondary air has a good mixing state, but by adjusting the flow rate of the auxiliary air AA, the degree of narrowing of the combustible waste flow through the combustible waste flow path 3 can be adjusted, so that the self-combustibility can be adjusted independently during operation The degree of diffusion of the combustible waste RF ejected from the waste blowing device 2.

^{In view of this situation, the flow rate V (Nm 3} /hour) of the auxiliary air AA flowing from the auxiliary air inlet 5 into the combustible waste flow path 3 per unit time is preferably the primary air flow rate V flowing through the combustible waste flow path 3 ₀ (Nm ³ /hour) of 5% to 65% by volume. When V/V _{0 is} less than 5% by volume, the narrowing effect of the combustible waste stream using auxiliary air AA cannot be obtained. In addition, when V/V ₀ exceeds 65% by volume, there is a combustible waste stream. The degree of diffusion of the flammable waste increases, and some combustible waste RF collides with the inner wall of the upper part of the cement kiln. In addition, when the combustible waste diffuses to the extent that part of the combustible waste RF collides with the inner wall of the kiln, the flame shape of the burner for the cement kiln is greatly confused, and the quality of the cement clinker becomes poor. It is stable, and the heat loss of the refractory bricks in the cement kiln becomes larger.

In addition, when the degree of diffusion of the combustible waste RF ejected from the combustible waste blowing device 2 is constant when the flow rate of the auxiliary air AA is constant, the position of the auxiliary air inlet 5 can be changed (more specifically, Y-direction position) for adjustment.

In view of this situation, the distance in the Y direction from the blowing port (end) of the combustible waste flow path 3 to the auxiliary air inflow port 5 is preferably in the range of 10 mm to 600 mm. When the distance is less than 10 mm, the degree of diffusion of the fluid of the combustible waste RF increases and a part of the combustible waste RF collides with the inner wall of the upper part of the cement kiln. In addition, when the distance in the Y direction from the blowing port of the combustible waste flow path 3 to the auxiliary air inlet 5 exceeds 600 mm, the diffusion effect of the combustible waste RF using the auxiliary air AA may disappear.

Regardless of whether auxiliary air AA is introduced, by adjusting the elevation angle φ of the upward slope 8 provided on the bottom surface of the combustible waste flow path 3, the spray angle of the combustible waste flow sprayed from the combustible waste flow path 3 can also be adjusted. By appropriately adjusting the spray angle of the combustible waste stream, the floating state of the combustible waste RF in the cement kiln can be sustained for a long time.

In view of this situation, the angle (elevation angle φ) of the upward slope 8 is preferably in the range of 1° to 4°. When the elevation angle φ of the upward slope 8 is less than 1°, only the auxiliary air AA must be used to make the combustible waste flow upward, and the energy required for blowing the auxiliary air AA must be excessive. In addition, when the elevation angle φ of the upward slope 8 is greater than 4°, the diffusion effect of the auxiliary air AA will be excessively applied. As a result, a part of the combustible waste RF may collide with the upper inner wall of the cement kiln.

In addition, the reason why the ratio of the flow rate of the auxiliary air AA in the upper and lower directions is important is that by adjusting the ratio of the downward auxiliary air flow rate and the upward auxiliary air flow rate, the spraying direction of the combustible waste RF can be adjusted up and down, thereby enabling The direction of the combustible waste RF ejected from the combustible waste blowing device 2 is further vertically upward. As a result, the floating state of the combustible waste RF sprayed in a good diffusion state by the auxiliary air AA can be adjusted to a better state.

In view of this situation, the ratio r of the downward auxiliary air flow rate flowing in from the vertical upper side of the horizontal plane containing the shaft center to the upward auxiliary air flow rate flowing in from the vertical lower side of the horizontal plane containing the shaft center is preferably set to 0.5 to 1.0 range. When the ratio r is less than 0.5, the combustible waste stream blows upward from the lower side, and a part of the combustible waste RF collides with the upper inner wall of the cement kiln. In addition, when the ratio r is greater than 1.0, that is, when the downward auxiliary air flow rate is greater than the upward auxiliary air flow rate, a downward force is applied to the combustible waste flow, plus the upward effect of the upward slope, and there is a A situation in which the flow of combustible waste produces a great deal of chaos.

As described above, according to the present invention, before the operation of the combustible waste blowing device 2, the elevation angle φ of the upward slope 8, the position of the auxiliary air inlet 5 and the inflow angle θ are set within the range shown in Table 1. Furthermore, when the combustible waste blowing device 2 is operating, the auxiliary air flow V and the ratio r of the auxiliary air flow from the vertical direction are adjusted by the blower and/or the flow adjustment valve, so that the combustible waste can be removed The operating conditions of the blowing device 2 are optimized, and the flame state of the burner for the cement kiln becomes stable. Furthermore, in the case of the combustible waste blowing device 2 shown in FIG. 6 without the auxiliary air flow path 4 and the auxiliary air inlet 5, by adjusting the elevation angle φ of the upward slope 8, the cement The flame state of the kiln burner becomes stable.

Then, the combustion simulation of the rate of land combustion (the drop rate in the kiln) of the combustible waste RF (soft plastic here) when the situation of each item in Table 1 is changed is explained.

Specifically, when the specifications and operating conditions of the above-mentioned cement kiln burner device 1 are fixed, simulation (software: manufactured by ANSYS JAPAN, FLUENT) is used to verify the situation of changing the items in Table 1. The setting values of each item in the simulation are shown in Table 2. Furthermore, as an example (comparative example) where the upward slope 8 is not provided and the auxiliary air AA is not used (comparative example), two levels (5 t/h, 2 t/h) of the combustible waste RF treatment amount are set.

The kiln drop rate of the combustible waste RF (soft plastic with a diameter of 30 mm and a thickness of 0.5 mm) obtained as a result of this simulation is shown in Table 3. Examples 1 to 5 and Comparative Examples 1 to 2 The gas temperature distribution in the kiln is shown in Figure 8.

[Table 2] Elevation angle of upward slope 8 φ (°) Auxiliary air flow ((auxiliary air flow)/(primary air flow through combustible waste flow path 3)) (vol%) The ratio of the auxiliary air flow in the upper and lower directions r (downward auxiliary air flow)/(upward auxiliary air flow) Position of auxiliary air inlet 5 (distance from the end) (mm) Inflow angle θ of auxiliary air AA (°) Example 1 2 -(No auxiliary air) -(No auxiliary air) -(No auxiliary air) -(No auxiliary air) Example 2 2 25 0.80 50 90 Example 3 2 25 0.67 50 90 Example 4 4 25 0.80 50 90 Example 5 2 50 0.80 50 90 Comparative example 1 (RF: 5 t/hour) -(No upward slope) -(No auxiliary air) -(No auxiliary air) -(No auxiliary air) -(No auxiliary air) Comparative example 2 (RF: 2 t/hour) -(No upward slope) -(No auxiliary air) -(No auxiliary air) -(No auxiliary air) -(No auxiliary air)

[table 3] The drop rate of combustible waste RF in the kiln (mass%) Example 1 2.1 Example 2 1.4 Example 3 0.8 Example 4 0.6 Example 5 0.0 Comparative example 1 3.0 Comparative example 2 0.5

According to the results in Table 3, it can be confirmed that the levels of each of Examples 1 to 5 are sufficient compared to the level of Comparative Example 1 where the condition of the treatment amount of combustible waste RF is set to 5 t/hour. Reduce the drop rate of combustible waste RF in the kiln. It can be confirmed that in Example 1, which does not use auxiliary air AA, the drop rate in the kiln can be reduced compared to Comparative Example 1 under the current operating conditions. By installing an upward slope 8, it is possible to suppress combustible waste. The effect of burning on the ground of the object RF. Furthermore, according to Examples 2 to 5 in which auxiliary air AA was introduced in addition to the upward slope 8, compared with Example 1, the drop rate in the kiln was further reduced.

According to Examples 3 to 5, compared with Comparative Example 1, the value of the drop rate in the kiln can be reduced to 1/3 or less. In particular, according to Example 5, the drop rate in the kiln can reach 0%. Thus, it was confirmed that the combustible waste blowing device and the operation method of the combustible waste blowing device of the present invention can effectively burn the combustible waste RF.

In addition, in the temperature distribution of the gas in the cement kiln shown in Fig. 8, the temperature distribution of the gas in each of Examples 1 to 5 and the current operating conditions set the treatment capacity of combustible waste RF to 2 t/ The situation of Comparative Example 2 for hours is almost the same. The operating conditions of Comparative Example 2 were that the supply amount of combustible waste RF was set to be less than that of the respective examples, and the drop rate of combustible waste RF in the kiln was 0.5% by mass, and the kiln burner was in good combustion state. On the other hand, in Comparative Example 1, where the RF treatment amount of combustible waste (5 t/hour) is the same as that of this example under the current operating conditions, the temperature of the gas in the cement kiln is greatly reduced, and the combustible waste The drop rate in the RF kiln is 3.0% by mass, and a large amount of combustible waste RF is burned on the ground. It can be confirmed that the present invention can effectively use combustible waste RF as auxiliary fuel without greatly changing the temperature distribution of the gas in the cement kiln.

That is to say, with the present invention, the optimal combustion state of the burner for cement kiln can be easily maintained, and combustible waste can be effectively used as auxiliary fuel.

In addition, the installation number and installation position of the auxiliary air inflow port provided with the combustible waste blowing device are not limited to the structure of the said embodiment.

1: Burner device for cement kiln 2: Combustible waste blowing device 3: Combustible waste flow path 3c: The axis of the combustible waste flow path 4: auxiliary air flow path 4-1, 4-2: auxiliary air flow path 4-3, 4-4, 4-5, 4-6, 4-7, 4-8: auxiliary air flow path 5: Auxiliary air inlet 5-1, 5-2, 5-3, 5-4, 5-5, 5-6, 5-7, 5-8, 5-9, 5-10: auxiliary air inlet 5-11, 5-12, 5-13, 5-14, 5-15, 5-16: auxiliary air inlet 6: Partitioning member 7: Auxiliary air feed 8: upward slope 11: Air piping 12: Combustible waste conveying piping 13: Air piping 21: Flow path for solid powder fuel 22, 23, 24: air flow path 22a: Slewing Wing 31: Flow path for oil 113, 114, 118: branch pipe 135,136,137: branch pipe AA: auxiliary air B113, B114, B135, B136, B137, B118: flow adjustment valve F1, F2, F3: blower RF: Combustible waste θ: Inflow angle of auxiliary air φ: Elevation angle of upward slope

Fig. 1 is a diagram schematically showing the central part of the front end of an embodiment of a burner device for a cement kiln equipped with a combustible waste blowing device of the present invention. [Fig. 2A] is a longitudinal cross-sectional view schematically showing the tip portion of an embodiment of the combustible waste blowing device of the present invention. [Fig. 2B] is a cross-sectional view schematically showing the front end portion of an embodiment of the combustible waste blowing device of the present invention. [Figure 3] is a partial enlarged view of Figure 2A. [Fig. 4A] is a longitudinal cross-sectional view schematically showing the tip portion of another embodiment of the combustible waste blowing device of the present invention. [Fig. 4B] is a cross-sectional view schematically showing the front end of another embodiment of the combustible waste blowing device of the present invention. [Fig. 5] A diagram schematically showing an example of the structure of the combustible waste blowing device shown in Figs. 4A and 4B. Fig. 6 is a diagram schematically showing the center part of the front end of another embodiment of a burner device for a cement kiln equipped with a combustible waste blowing device of the present invention. Fig. 7 is a diagram schematically showing the front end of an embodiment of a burner device for a cement kiln equipped with a combustible waste blowing device for simulated use. [Figure 8] shows the use of the combustible waste blowing device shown in Figure 7, under the operating conditions shown in Table 2, the quantitative use of waste plastic with a diameter of 30 mm as an auxiliary fuel relative to the main fuel (pulverized coal) This is a graph of the simulation results of the gas temperature distribution in the cement kiln related to Examples 1 to 5 and Comparative Examples 1 to 2.

1: Burner device for cement kiln

2: Combustible waste blowing device

3: Combustible waste flow path

4: auxiliary air flow path

5: Auxiliary air inlet

8: upward slope

21: Flow path for solid powder fuel

22: Air flow path

22a: Slewing Wing

31: Flow path for oil

Claims (11)

A combustible waste blowing device, which is equipped with at least one air flow path inside the flow path for solid powder fuel, which can be attached to a burner device for cement kilns, and is characterized in that it has: The combustible waste flow path is arranged on the inner side of the air flow path of the innermost shell, and is arranged parallel to the axial direction of the burner device for the cement kiln, for conveying combustible waste flow, and The combustible waste flow path has an upward slope toward the blowing port near the blowing port so that the width of the flow path in the vertical direction becomes narrower as it approaches the blowing port. Such as the flammable waste blowing device of claim 1, in which, The end of the inclined surface opposite to the blowing port in the axial direction of the combustible waste flow path is located at a distance of 150 mm to 2000 mm from the blowing port, and the elevation angle is 1° to 4°. If the combustible waste blowing device of claim 1 or 2, its The combustible waste flow path is provided with an auxiliary air inlet that allows the auxiliary air flow to flow into the combustible waste flow path toward the axis of the combustible waste flow path at the position where the inclined surface is formed, and The auxiliary air inlets are arranged at a plurality of locations in the circumferential direction. Such as the combustible waste blowing device of claim 3, in which, The auxiliary air inlets are arranged at a plurality of locations, and when these locations are cut along a plane orthogonal to the axis of the combustible waste flow path in the vertical direction, the axis of the combustible waste flow path is included. level. Such as the combustible waste blowing device of claim 4, in which, The combustible waste flow path is such that the combustible waste flow can be reduced in the axial direction by the auxiliary air flow flowing in from the auxiliary air inlet, and the combustible waste flow can be ejected upward in the vertical direction. Way of composition. Such as the combustible waste blowing device of claim 3, in which, The auxiliary air inlet is arranged in a range of 10 mm to 600 mm away from the blowing inlet of the combustible waste flow path. A method for operating a combustible waste blowing device as in claim 1 or 2, wherein: The combustible waste stream is sprayed upward from the combustible waste flow path in a vertical direction relative to the horizontal plane. Such as the operation method of the combustible waste blowing device in claim 7, in which: The combustible waste flow path is provided with an auxiliary air inlet that allows the auxiliary air flow to flow into the combustible waste flow path toward the axis of the combustible waste flow path at the position where the inclined surface is formed, and The auxiliary air inlets are arranged at a plurality of locations in the circumferential direction, The flow rate of upward auxiliary air flowing in from the lower side in the vertical direction of the horizontal plane is greater than the flow rate of downward auxiliary air flowing in from the upper side in the vertical direction of the horizontal plane. Such as the operation method of the combustible waste blowing device of claim 8, in which: The total amount of air flow into the combustible waste flow path from the auxiliary air inlet is 5 vol% to 65% by volume of the primary air flow that circulates in the combustible waste flow path. Such as the operation method of the combustible waste blowing device of claim 8 or 9, in which, The ratio of the above-mentioned downward auxiliary air flow rate to the above-mentioned upward auxiliary air flow rate is 0.5 to 1.0. Such as the operation method of the combustible waste blowing device of claim 8 or 9, in which, The inflow angle of the auxiliary air flow flowing into the combustible waste flow path is greater than 0° and 90° or less based on the transport direction of the combustible waste flow transported in the combustible waste flow path.

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